Description
Species Name -Teredo navalis Linnaeus 1758.
Synonymy - P. teredo Mueller 1776; T. vulgaris Lamarack 1801; T. sellii van der Hoeven 1850; S. marina Jeffreys 1860; T. japonica Clessin 1893; T. beachii Bartsch 1921; T. beaufortana Bartsch 1922; T. novagliae Bartsch 1922; T. sinensis Roch 1929; T. pocilliformis Roch 1931; T. borealis Roch 1931.
Potentially Misidentified Species - Psiloteredo megotara (as Teredo megotara) Hanley and Nototeredo knoxi Bartsch (as Teredo sigerfoosi) have been identified from test panels exposed from the Chesapeake lightship (36 degrees, 59 minutes N. Lat.; 75 degrees 42 minutes W. Long.) (Brown 1953).
Taxonomy
Kingdom | Phylum | Class | Order | Family | Genus |
---|---|---|---|---|---|
Animalia | Mollusca | Bivalvia | Myoida | Teredinidae | Teredo |
Synonyms
Invasion History
Chesapeake Bay Status
First Record | Population | Range | Introduction | Residency | Source Region | Native Region | Vectors |
---|---|---|---|---|---|---|---|
1878 | Established | Stable | Introduced | Regular Resident | Unknown-Marine | Unknown-Marine | Shipping(Fouling Community) |
History of Spread
The status of Teredo navalis (Naval Shipworm) in Northwest Atlantic waters has been debated, but we feel that historical evidence supports the introduction of this shipworm to both sides of the Atlantic (Coomans 1962; Reise et al. 1999). Teredo navalis was definitely introduced to the Northeast Pacific and probably to many other parts of the world in the hulls of wooden ships (Carlton 1992). Carlton (1992) treated this species as: 'Cryptogenic in NW Atlantic; early American records include reports both from visiting vessels (Russell 1839; MA) and from established populations (DeKay 1843; NY).' Subsequently, re-examination of historical evidence has caused Ruiz et al. (2000) to change the status of this species to a definite introduction.
The reasons for treating this species as a clear introduction are: (1) Established populations referred to by DeKay (1843) south of NY were probably B. gouldi, which was apparently not distinguished from T. navalis before the 1860s. The description of Bankia fimbriata (as Xylotria fimbriata) clarified distinctions between two groups of coastal shipworms, and provided a name which was then used for the animal later described as B. gouldi (Tryon 1862; Tryon 1873). Tryon mentions that these species were formerly confused. (2) Early reports of T. navalis from New England are confined to ships; e.g. 'Found in the sheathing of vessels from foreign seas' (Russell 1839) 'From a British frigate sunk during the Revolutionary war' (Tryon 1862); 'The only locality in which I have found this species is an old half-buried wreck near the entrance of the harbor' (Perkins 1871). By the late 19th century, it apparently became widespread in New England waters (Verrill and Smith 1874; Johnson 1915). (3). Teredo navalis was absent in wood of a 5,000 yr-old fishweir in Boston, though B. gouldi was found (Johnson et al. 1942). (4). Teredo navalis was treated as an introduced species in the North Sea (Reise et al. 1999), where its introduction was apparently responsible for a massive attack on Dutch dikes in the 17th century. This species has been transported by ships for so many centuries that its native region is unknown.
Northwest Atlantic records are summarized below:
Gulf of Maine In ports of Essex County MA (Massachusetts Bay), 1839, T. navalis was 'found in the sheathing of vessels from foreign seas' (Russell 1839). Later, it was abundant in test boards at Halifax Nova Scotia, Portland ME, and Boston MA, in 1945-52 (Brown 1953).
Woods Hole, MA (Vineyard Sound; Buzzards Bay) - The first published record is from Verrill (1871). 'The common species of shipworm at Woods Hole as identified by Koifoid and Clapp is Teredo navalis. The date of its first appearance in the region is not known' (Grave 1928). It was abundant in test boards at Woods Hole from 1936-52 (Brown 1953).
Long Island Sound- The first record of T. navalis is from New Haven Harbour CT in 1869 'The only locality in which I have found this species is an old half-buried wreck near the entrance of the harbor' (Perkins 1871). It was abundant in test boards at Fishers Island and various sites around New York Harbor, 1934-52 (Brown 1953).
Chesapeake Bay-adjacent Ocean Regions- Teredo navalis was rare in Chincoteague Bay, but abundant at Ocean City MD in 1952 (Scheltema and Truitt 1956).
Chesapeake Bay (Lower Bay) - At Fort Wool, 1878; 'Broken shells of this creature occur among the rubbish at the bottom of the water. It is quite common in the Elizabeth River and will no doubt be found in the submerged part of the piles which support the wharf' (Uhler 1878). It was also reported from Hampton Roads, 1949 (Ferguson and Jones 1949). Andrews (1956) stated that 'Teredo navalis is rare in the Chesapeake Bay and is not the common shipworm', but specimens of T. navalis were found in test boards in the Elizabeth River, 1944-52, at Norfolk and Portsmouth VA. They were not found in test boards at Lee Hall in the James River, or at Baltimore or Annapolis (Brown 1953).
South of Chesapeake Bay, T. navalis is found in coastal waters of NC and southward to FL, TX, the Bahamas, and Puerto Rico (Brown 1953).
History References - Andrews 1956; Brown 1953;Carlton 1992; DeKay 1843 Coomans 1962; Ferguson and Jones 1949; Grave 1928; Johnson 1915; Johnson et al. 1942; Perkins 1871; Reise et al. 1999; Russell 1839; Scheltema and Truitt 1956; Tryon 1862; Tryon 1873; Uhler 1878; Verrill and Smith 1874; Wass et. al. 1972.
Invasion Comments
Ecology
Environmental Tolerances
For Survival | For Reproduction | |||
---|---|---|---|---|
Minimum | Maximum | Minimum | Maximum | |
Temperature (ºC) | 0.0 | 30.0 | 11.0 | |
Salinity (‰) | 5.0 | 45.0 | 9.0 | |
Oxygen | anoxic | |||
pH | ||||
Salinity Range | poly-eu |
Age and Growth
Male | Female | |
---|---|---|
Minimum Adult Size (mm) | 50.0 | |
Typical Adult Size (mm) | 200.0 | |
Maximum Adult Size (mm) | 400.0 | |
Maximum Longevity (yrs) | 2.0 | |
Typical Longevity (yrs | 1.5 |
Reproduction
Start | Peak | End | |
---|---|---|---|
Reproductive Season | |||
Typical Number of Young Per Reproductive Event |
|||
Sexuality Mode(s) | |||
Mode(s) of Asexual Reproduction |
|||
Fertilization Type(s) | |||
More than One Reproduction Event per Year |
|||
Reproductive Startegy | |||
Egg/Seed Form |
Impacts
Economic Impacts in Chesapeake Bay
Teredo navalis (Naval Shipworm) is uncommon in Chesapeake Bay proper, and is probably not a major contributor to the deterioration of wooden structures there. It was rare in Chincoteague Bay, but abundant in test boards at Ocean City, where it appeared to pose a serious threat to wooden structures (Scheltema and Truitt 1956). This shipworm is economically important in the Atlantic waters adjacent to the Chesapeake Bay.
References- Scheltema and Truitt 1956
Economic Impacts Outside of Chesapeake Bay
Teredo navalis (Naval Shipworm) is probably the most widespread marine wood borer in the world, and has been a major factor in human maritime activities for many centuries (Turner 1966). In the 18th century in the Netherlands, shipworms caused extensive damage to wooden seawalls, which had to be replaced by stone. The worms were declared to be a plague sent by God (Reise et al. 1999). In the 1920s, an outbreak of T. navalis in San Francisco Bay caused an estimated $615 million dollars (in 1992 dollars) in damage (Cohen and Carlton 1995). In 1946, shipworms were reported to cause an annual $55 million ($500 million in current dolars) of damage to waterfront structures in United States, 1946 (Clapp 1946, cited by Scheltema & Truitt 1954).
References- Cohen and Carlton 1995; Reise et al. 1999; Scheltema and Truitt 1954; Turner 1966
Ecological Impacts on Chesapeake Native Species
Ecological impacts of Teredo navalis (Naval Shipworm) on native biota may be limited by its low abundance in the Bay proper, but it is an abundant and important woodborer in adjacent Atlantic waters (Scheltema and Truitt 1956).
Competition with the native Bankia gouldi (Gould's Shipworm) is possible, but has not been documented. Competition would be restricted to polyhaline parts of the lower Bay, because of T. navalis' preference for high salinities (Brown 1953; Wass et. al. 1972). In Barnegat Bay, both species overlap, but B. gouldi dominates in the western parts of the bay while T. navalis is the predominant form in the more saline inner parts (Richards et al. 1984).
Habitat Change - Boring animals may alter habitats by breaking up woody debris, opening cavities, etc., permitting other animals to use the wood for shelter (Turner 1984).
Herbivory - Boring animals speed the recycling of wood in the marine environment, allowing it to enter foodwebs (Turner 1984).
References - Brown 1953; Richards et al. 1984; Turner 1984; Wass et. al. 1972
Ecological Impacts on Other Chesapeake Non-Native Species
Ecological impacts of Teredo navalis (Naval Shipworm) on exotic biota may be limited by its low abundance in the Bay proper, but it is an abundant and important woodborer in adjacent Atlantic waters (Scheltema and Truitt 1956).
Competition - Competition is possible with T. bartschi (Bartsch's Shipworm) and T. furcifera, but has not been documented. Probably, temperature and salinity are more important limiting factors for the subtropical species (Hoagland 1986; Richards et al. 1984).
References - Hoagland 1986; Richards et al. 1984; Scheltema and Truitt 1956
References
Bartsch, Paul (1923) The status of Teredo beachi and Teredo navalis, Science 57: 692Brown, Dorothy J. (1953) Sixth Progress Report on marine borer activity in test boards operated during 1952, Report No. 8511 , Duxbury, Massachusetts. Pp.
Carlton, James T. (1992) Introduced marine and estuarine mollusks of North America: An end-of-the-20th-century perspective., Journal of Shellfish Research 11: 489-505
Chanley, Paul; Andrews, J. D. (1971) Aids for identification of bivalve larvae of Virginia, Malacologia 11: 45-119
Clapp, William F. (1923) New species of Teredo from Florida, Proceedings of the Boston Society of Natural History 37: 31-38
Coomans, H. E. (1962) The marine mollusk fauna of the Virginian area as a basis for defining zoogeographical provinces., Beaufortia 9: 83-104
Culliney, J. L. (1975) Comparative larval development of the shipworms Bankia gouldi and Teredo navalis, Marine Biology 29: 245-251
Ferguson, F. F.; Jones, E. R. (1949) A survey of the shoreline fauna of the Norfolk Peninsula., American Midland Naturalist : 436-446
Grave, B. H. (1928) Natural history of shipworm, Teredo navalis, at Woods Hole, Massachusetts, Biological Bulletin 55: 260-282
Hillman, Robert E.; Ford Susan E.; Haskin, Harold H. (1990) Minchinia teredinis n. sp. (Balanosporida, Haplosporidiidae), a parasite of teredinid shipworms, Journal of Protozoology 37: 364-368
Hoagland, K. Elaine (1983) Life history characteristics and physiological tolerances of Teredo bartschi, a shipworm introduced into two temperate zone nuclear power plant effluents., In: Sengupta, N. S., and Lee S. S.(Eds.) Third International Waste Heat Conference.. , Miami Beach, FL. Pp. 609-622
Hoagland, K. Elaine (1986a) Effects of temperature, salinity, and substratum on larvae of the shipworms Teredo bartschi Clapp and T. navalis Linnaeus (Bivalvia: Teredinidae), American Malacological Bulletin 4: 89-99
Johnson, Charles W. (1915) Fauna of New England. 13. List of the Mollusca, Occasional Papers of the Boston Society of Natural History 7: 1-223
Johnson, Charles W. (1934) List of marine mollusca of the Atlantic coast from Labrador to Texas, Proceedings of the Boston Society of Natural History 40: 1-204
Perkins, George H. (1871) Molluscan fauna of New Haven. A critical review of all the marine, fresh water and land Mollusca of the region, with descriptions of many of the living animals and of two new species. Part II: Acephala and Bryozoa., Proceedings of the Boston Society of Natural History 13: 138-163
Reise, K.; Gollasch, S.; Wolff, W.J. (1999) Introduced marine species of the North Sea coasts., Helgoländer Meeresuntersuchungen 52: 219-234
Richards, Beatrice R.; Hillman, Robert E.; Maciolek, Nancy J. (1984) Shipworms, In: Kennish, Michael J.; Lutz, Richard A.(Eds.) Lecture Notes on Coastal and Estuarine Studies - Ecology of Barnegat Bay, New Jersey. , New York. Pp. 201-225
Russell, John Lewis (1839) Familiar notice of some of the shells found in the limits of Essex County, Massachusetts: with reference to descriptions and figures, Journal of the Essex County Natural History Society : 47-77
Scheltema, Rudolf S.; Truitt, R. V. (1954) Ecological factors related to the distribution of Bankia gouldi Bartsch in Chesapeake Bay, Chesapeake Biological Laboratory Publication 100: 1-31
Scheltema, Rudolf S.; Truitt, R. V. (1956) The shipworm Teredo navalis in Maryland coastal waters, Ecology 37: 841-843
Sigerfoos, Charles P. (1907) Natural history, organization, and late development of the Teredinidae, or ship-worms, Bulletin of the Bureau of Fisheries 27: 191-231, pls. 7-21
Tryon, George W., Jr. (1862) Monograph of the Teredidae, Proceedings of the Academy of Natural Sciences of Philadelphia 14: 453-481
Tryon, George Washinngton (1873) American marine conchology: or, Descriptions of the shells of the Atlantic coast of the United States from Maine to Florida, None , Philadelphia. Pp. None
Turgeon, D.D.; Bogan, A.E.; Coan, E.V.; Emerson, W.K.; Lyons, W.G.; Pratt, W.L.; Roper, E.F.E.; Scheltema, A.; Thompson, F.G.; Williams, J.D. (1988) Common and Scientific Names of Aquatic Invertebrates from the United States and Canada: Mollusks, , Bethesda, Maryland. Pp. 227 pages
Turner, Ruth D. (1966) A survey and illustrated catalogue of the Teredinidae (Mollusca: Bivalvia), , Cambridge. Pp.
Turner, Ruth D. (1971) Identification of marine wood-boring molluscs., , Paris. Pp.
Turner, Ruth D. (1984) An overview of research on marine borers: past progress and future direction., In: Costlow, J.D./Tipper, R. C.(Eds.) Proceedings of the Symposium on Marine Biodeterioration. , Annapolis, MD. Pp.
Uhler, P. R. (1878) List of animals observed at Fort Wool, Va., , Baltimore. Pp.
Verrill, A.E.; Smith, S.I. (1873) VIII. Report upon the invertebrate animals of Vineyard Sound and the adjacent waters, with an account of the physical characters of the region., 1 , . Pp. 1-757
Wass, Melvin L. (1972) A checklist of the biota of lower Chesapeake Bay, Special Scientific Report, Virginia Institute of Marine Science 65: 1-290